Abstract Chemical fertilizers are used everywhere, which often pollute the breeding sites of mosquitoes. In this laboratory study, the consequences on Aedes aegypti (L.) (Diptera: Culicidae) and Anopheles gambiae (Giles) (Diptera: Culicidae) of water-containing plant matter (PM) alone, or in association with an NPK type of fertilizer (PM+NPK), were evaluated. To obtain a 20% imaginal emergence of An. gambiae (IEt20), the bioassays carried out with PM have evidenced that its larvae need four times as much food as for Ae. aegypti larvae. The PM+NPK combinations significantly improve the survival rates of both mosquitoes multiplying the percentages of imaginal emergence by 1.7–3 (synergistic effect). The log-probit analysis of the adult emergence also reveals that the environments containing fertilizers accelerates by two to four times the development of the mosquito larvae. Aedes aegypti, Anopheles gambiae, plant material, fertilizer, synergistic effect The distribution of mosquito populations depends on the presence of breeding sites with suitable physicochemical and biological characteristics (Bentley and Day 1989; Barrera and Amador 2006; Darriet and Corbel 2008a,b). Aedes aegypti (L.) (Diptera: Culicidae) develops in small- to middle-sized domestic and peridomestic collections of clear water (Cordellier et al. 1977). Despite a recent proliferation inside cities (Barbazan et al. 1998, Dossou-Yovo et al. 1998), Anopheles gambiae (Giles) (Diptera: Culicidae) remains a lot more rural with breeding sites ranging from rice paddies to smaller puddles. Dengue fever, chikungunya, and zika are arboviral diseases transmitted to humans by Ae. aegypti (Hayes 2009, Reiter 2010, Akiner et al. 2016). An. gambiae transmits the Plasmodium responsible for malaria. Two billions of people still live in areas significantly plagued by this disease (WHO 2011). Both mosquitoes lay their eggs in water collections of varying nature. Still some factors related to the quality of the water will make some breeding sites more attractive than others. Deciduous and coniferous leaves, hay, and grass brewing have long been known for their attraction properties on mosquitoes (Chadee et al. 1993, Clement 2000, Darriet, 2014). The special attraction of Ae. aegypti gravid females to this type of breeding sites is partly determined by the presence of fertilizer in the water (Darriet and Corbel 2008a). As a matter of fact, fertilizers favor the growth of algae and bacteria that account for part of the mosquito larvae diet (Young et al. 2014). The fertilizers home gardeners and owners use the most contain nitrogen (N), phosphorus (P), and potassium (K). The water from plant watering, thus, enriched with NPK fertilizers seeps through the soil into the dishes placed under the pots. Those small yet numerous collections of domestic waters are well-known to the mosquito control services for hosting large populations of Aedes albopictus or Ae. aegypti (Delatte et al. 2008, Costa et al. 2012). Similarly, in farming areas, many mosquito species are also regularly exposed to massive concentrations of fertilizers and pesticides (Diabate et al. 2002, Sandford et al. 2005, Akogbeto et al. 2006). In rice paddies, the densities of Anopheles larvae were reported reaching peaks a few days after nitrogenous fertilizer was poured out at the time of transplanting (Victor and Reuben 2000, Mwangangi et al. 2006). In this laboratory study, we studied the growth rate of Ae. aegypti and An. gambiae according to whether the breeding sites contained plant matter and/or NPK fertilizer. The effects of the plant matter and fertilizer combinations were also determined in comparison with the activity of each component on its own (additive or synergistic interactions). Materials and Methods Mosquito Strains The insecticide-susceptible strains (SS) of Ae. aegypti (Bora) and An. gambiae (Kisumu = KIS) have been reared for more than 20 years in the Institute of Research for Development (IRD) insectarium in Montpellier (France). Plant Matter and NPK Fertilizer The plant material (PM) used in this study consisted of commercial rodent food (grassland hay) (Zolux, Domazan, France). This particular brand of hay had already been used in two previous research works focused on the biology of mosquitoes (Darriet et al. 2010, Darriet et al. 2012). The liquid NPK fertilizer 5-7-5 (Algoflash, Asnières sur Seine cedex, France) contained 5% of nitrogen (N) consisting in 3% of NO3− and 2% of NH4+; 7% of phosphorus (P) in the form of P2O5 and 5% of potassium (K) in the form of K2O. PM, NPK, and PM+NPK Compositions and Bioassays Procedures The quantities of plant material and NPK fertilizer selected for the constitution of larval environment are those that separately induced a low range (0–20%) of imaginal emergence on Ae. aegypti and An. gambiae. For the plant material, the quantities tested were 1000 mg/liter for Ae. aegypti (PM1) and 4000 mg/liter (PM4) for An. gambiae. For the fertilizer, four concentrations (NPK1: 4-6-4 mg/liter, NPK2: 17-23-17 mg/liter, NPK3: 33-47-33 mg/liter, and NPK4: 66-91-66 mg/liter) were tested on both mosquitoes. The PM+NPK combinations were done using the same concentrations as the PM or NPK alone. PM, NPK, and the different PM+NPK combinations were prepared in 0.0042 m3 plastic trays (length: 0.30 m; width: 0.20 m; depth: 0.07 m), each containing 1 liter of reverse osmotic water. Twenty-four hours after the preparation of the larval environments, 100 first instars larvae of Ae. aegypti or An. gambiae were counted and placed in a tray. Each artificial milieu was evaluated on a total of three replicates. Throughout the duration of the experiment, the trays were maintained at a temperature of 27 ± 2°C. Statistical Analyses Every day, female and male adults were counted in each environment to establish the percentages of imaginal emergence with a 95% CI (Vollset 1993). The experiment was stopped when all larvae or pupae died or emerged in adults. Then the percentages of females and males from the different environments were compared for the purpose of statistical analysis (Wilcoxon test using Statistica 2011). The larval environments allowing more than 20% of adult emergences were analyzed using the log-probit software (Raymond et al. 1997) to determine the duration of preimaginal developments leading to 20 and 50% of imaginal emergence (IEt20, 50). The results obtained for each combination were compared with the results theoretically expected in the absence of any interaction (additive effect). The expected mosquito emergence (Corbel et al. 2002) for each PM+NPK combination was calculated by 1 − (frequency of global mortality on PM by frequency of global mortality on NPK), the global mortality adding up the mortalities recorded among the larvae, the nymphs, and the adults that had drowned. Synergy (positive interaction) is evidenced when the observed mosquito emergence is significantly higher (chi-square test using Statistica 2011) than the expected mosquito emergence. Results Aedes aegypti Bioassays In the PM1 environment, adult emergence reached 19% after 55 d of larval development (Table 1). The log-probit analysis of the imaginal emergence along time assesses the time needed for 20% of adult Ae. aegypti to emerge (IEt20) at 58.8 d. For NPK1 to NPK4 concentrations, 2.7–3.3% adults emerged along the 61–66 d period. Table 1. Determination of imaginal emergence time 20% and 50% (IEt20 and IEt50) of Aedes aegypti and calculation of synergistic or additive effects of the PM1+NPK combinations Plant material and/or fertilizer quantities (mg/liter) Maximum duration of preimaginal development (d) IEt20 IEt50 Slope (± SE) Adult emergence % observed (95% CI) [expected] P* in d (95% CI) PM1 (1000) 55 58.8 (53.1–67.1) ND 2.0 (± 0.2) 19.0 (14.6–23.4) — NPK1 (4-6-4) 66 ND ND ND 0 — NPK2 (17-23-17) 3.0 (1.04–5.0) NPK3 (33-47-33) 3.3 (1.3–5.3) NPK4 (66-91-66) 61 2.7 (1.0- 4.8) PM1+NPK1 60 20.5 (18.2–23.0) ND 4.5 (± 0.02) 44.7 (39.1–50.3)c  <0.005 PM1+NPK2 15.5 (13.3–17.9) 45.1 (40.7–50.0) 1.8 (± 0.2) 53.7 (48.1–59.3)  PM1+NPK3 32.9 (29.5–36.7) ND 1.3 (± 0.1) 28.7 (23.4–33.8)  0.06 PM1+NPK4 50 20.4 (18.0–23.2) 1.3 (± 0.2) 33.3 (28.0–38.6)  <0.005 Plant material and/or fertilizer quantities (mg/liter) Maximum duration of preimaginal development (d) IEt20 IEt50 Slope (± SE) Adult emergence % observed (95% CI) [expected] P* in d (95% CI) PM1 (1000) 55 58.8 (53.1–67.1) ND 2.0 (± 0.2) 19.0 (14.6–23.4) — NPK1 (4-6-4) 66 ND ND ND 0 — NPK2 (17-23-17) 3.0 (1.04–5.0) NPK3 (33-47-33) 3.3 (1.3–5.3) NPK4 (66-91-66) 61 2.7 (1.0- 4.8) PM1+NPK1 60 20.5 (18.2–23.0) ND 4.5 (± 0.02) 44.7 (39.1–50.3)c  <0.005 PM1+NPK2 15.5 (13.3–17.9) 45.1 (40.7–50.0) 1.8 (± 0.2) 53.7 (48.1–59.3)  PM1+NPK3 32.9 (29.5–36.7) ND 1.3 (± 0.1) 28.7 (23.4–33.8)  0.06 PM1+NPK4 50 20.4 (18.0–23.2) 1.3 (± 0.2) 33.3 (28.0–38.6)  <0.005 Bold font indicates that the adult emergence differed statistically from the expected value. *P < 0.05 = synergistic effect of the PM and NPK combinations. P > 0.05 = additive effect. ND, not detectable. View Large In all the PM1+NPK combinations, the imaginal emergence occurred over a time span of 50–60 d yet with very different rates of emergence from one combination to another. The PM1+NPK1, PM1+NPK2, and PM1+NPK4 combinations considerably improved the living conditions of the mosquitoes compared with the two components separately (synergistic interaction, P < 0.005). PM1+NPK3 induced only an additive effect to the actions (P = 0.06). The IEt20 of the four combinations tested reveal that 20% of the adult Ae. aegypti emerge between 15 and 33 d, two to four times faster growth of the larvae compared with PM1 (58.8 d). PM1+NPK2 combination was the most productive combination in allowing three times as many adults to emerge compared with PM1. Besides, its 45 d IEt50 is 14 d shorter than the IEt20 of plant matter alone. Anopheles gambiae bioassays To get 19% of adult An. gambiae, its larvae had to be provided with four times as much plant matter (PM4) as what Ae. aegypti required to reach the same percentage of survival (PM1) (Table 2). The 4 g/liter rate allows the larvae of An. gambiae to complete their preimaginal cycle within 17 d only. The four NPK solutions tested having denied survival to all An. gambiae larvae. Consequently, the percentages of expected emergences in PM4+NPK combinations all equaled the percentage of adults recorded in PM4 (19.3%). Table 2. Determination of imaginal emergence time 20 and 50% (IEt20 and IEt50) of An. gambiae and calculation of the synergistic or additive effects of the PM4+NPK combinations Plant material and/or fertilizer quantities (mg/liter) Maximum duration of preimaginal development (d) IEt20 IEt50 Slope (± SE) Adult emergence (%) observed (95% CI) [expected] P* in d (95% CI) PM4 (4000) 17 16.2 (13.1–28.2) ND 1.0 (± 0.3) 19.3 (14.8–23.8) — NPK1 (4-6-4) — ND ND ND 0 — NPK2 (17-23-17) NPK3 (33-47-33) NPK4 (66-91-66) PM4+NPK1 14 7.3 (6.6–7.8) 11.8 (11.4–12.3) 4.0 (± 0.03) 59.7 (54.2–65.2) [19.3] <0.005 PM4+NPK2 11 9.0 (8.8–9.2) 10.8 (10.6–11.2) 10.6 (± 0.8) 49.3 (43.6–55.3)  PM4+NPK3 14 ND ND ND 15.0 (11.0–19.0) [19.3] 0.14 PM4+NPK4 11 15.0 (11.0–19.0) [19.3] Plant material and/or fertilizer quantities (mg/liter) Maximum duration of preimaginal development (d) IEt20 IEt50 Slope (± SE) Adult emergence (%) observed (95% CI) [expected] P* in d (95% CI) PM4 (4000) 17 16.2 (13.1–28.2) ND 1.0 (± 0.3) 19.3 (14.8–23.8) — NPK1 (4-6-4) — ND ND ND 0 — NPK2 (17-23-17) NPK3 (33-47-33) NPK4 (66-91-66) PM4+NPK1 14 7.3 (6.6–7.8) 11.8 (11.4–12.3) 4.0 (± 0.03) 59.7 (54.2–65.2) [19.3] <0.005 PM4+NPK2 11 9.0 (8.8–9.2) 10.8 (10.6–11.2) 10.6 (± 0.8) 49.3 (43.6–55.3)  PM4+NPK3 14 ND ND ND 15.0 (11.0–19.0) [19.3] 0.14 PM4+NPK4 11 15.0 (11.0–19.0) [19.3] Bold font indicates that the adult emergence differed statistically from the expected value. *P < 0.05 = synergistic effect of the PM and NPK combinations. P > 0.05 = additive effect. ND, not detectable. View Large The percentages of adults emergences observed in PM4+NPK1 and PM4+NPK2 environments (59.7% and 49.3%, respectively) were way above (P < 0.005) the value expected (synergistic interaction). The log-probit analysis of the imaginal emergence has shown that for both combinations the IEt20 were two times less with plant matter alone (PM4). IEt50 themselves showed that 50% of the adults emerged after 11 and 12 d (as opposed to 17 d for PM4). As for PM4+NPK3 and PM4+NPK4, the comparison between the expected values and the ones actually observed only showed an additional effect of the interaction (P = 0.14). Female and male emergences No significant difference was recorded between the percentages of imaginal emergence of females and males (P > 0.05) whatever the nature of the breeding sites (Fig. 1). Because the sex ratios are identical for Ae. aegypti and An. gambiae, it shows that males and females emerge in equal quantities, whatever the composition of the breeding sites. Figure 1. View largeDownload slide Percentages (95% CI) of males and females mosquitoes whose larvae lived in environments containing plant material alone or in combination with NPK fertilizer. Figure 1. View largeDownload slide Percentages (95% CI) of males and females mosquitoes whose larvae lived in environments containing plant material alone or in combination with NPK fertilizer. Discussion Mosquito larvae breed in water collections whose physicochemical and biological characteristics differ a lot from one spot to another (Bentley and Day 1989; Darriet and Corbel 2008a,b; Darriet et al. 2010; Darriet et al. 2012). Although the nitrogen, phosphorus, and potassium alone cannot provide for the nutritional needs of the mosquito larvae, adding a chemical fertilizer into water already carrying plant material considerably increases the survival rate of these mosquitoes, multiplying by 1.7–3% of imaginal emergence (synergistic effect). The log-probit analysis of the adult apparitions also reveals a faster development of the larvae in PM+NPK combinations. The faster growth of the larvae in this type of environments partly comes from the production in the water of an organo-mineral complex abundant in nutrients (organic nitrogen and carbon, ammoniacal nitrogen [NH4+], nitric nitrogen [NO3−], phosphorus, and potassium) that favors the development of bacteria, algae, and fungi (Darriet et al. 2010; Hao et al. 2010). This supplementary food biomass of the breeding sites is crucial for the mosquito larvae because they cannot digest cellulose (Clements 2000). Ae. aegypti larvae not only grow in urban water collections of medium to larger size (barrels, cisterns, jars…) but also live in smaller breeding sites (vases, gutters, cans, tires, and plant pot saucers) where water volumes can easily dry up. Whether in urban or residential areas, there are many water collections polluted by fertilizers, yet plant pot saucers are undoubtedly the most polluted of all breeding sites for Ae. aegypti. In Brazil and Argentina, the plant pot saucers represented 4–14% of the identified breeding sites for Ae. aegypti larvae and pupae (Maciel-de-Freitas and Lourenço-de-Oliveira 2011, Costa et al. 2012). In the field, many small breeding sites are characterized by waters containing lots of plant material and fertilizers which favors the growth of Ae. aegypti and Aedes albopictus larvae (Delatte et al. 2008, Darriet et al. 2010). The faster growth of the larvae should thus allow the imaginal emergence before the water has completely dried up. An. gambiae larvae also can live just as well in rice paddies water and ponds as in smaller water collections such as puddles, footprints, or animal tracks. Similarly, where the waters contain plant matter and fertilizers, the survival rate of the mosquito is greater (synergistic effect) while the time of larval development is shorter. One hundred and eighty million tons of fertilizers (FAO 2012) and 2.4 million tons of pesticides (Grube 2011) are being used every year worldwide. Attracted by the fertilizers the mosquitoes preferentially lay their eggs in water collections that contain some (Darriet and Corbel 2008a, Young 2014, Kibuthu et al. 2016). The selection pressure induced by the agricultural inputs is huge, and the resistance mechanisms present in the mosquitoes are selected all the more rapidly and efficiently as the mineral fertilizations and the insecticide treatments are frequent within a time span. One of the vector control strategies to promote for the environments containing plant matter and fertilizers to produce fewer mosquitoes is to add a chemical or biological larvicide to the fertilizer, which kills the mosquito larvae right out from hatching. With less than 5% imaginal emergence, the fertilizer and spinosad combination treatment remained effective for 30 d on Ae. aegypti. Both fertilizer and pyriproxyfen or diflubenzuron combinations were effective for 45 d (Darriet 2016). Nowadays the diseases transmitted by mosquitoes kill many people worldwide. As for the interface agriculture/public health, there is still a huge research area that has only partly been explored. The synergy of such a partnership between the scientists, the rice-growers, and the vector control services would initiate pluridisciplinary research programs whose goal would be to protect the crops while reducing the mosquito populations as much as possible. Acknowledgments Special thanks to Hélène Darriet for kindly translating this French paper into English. References Cited Akiner, M. M., Demirci B., Babuadze G., Robert V., and Schaffner F.. 2016. Spread of the invasive mosquitoes Aedes aegypti and Aedes albopictus in the Black Sea region increases risk of chikungunya, dengue, and zika outbreaks in Europe. PLos Negl Trop Dis . 10: e0004664. Google Scholar CrossRef Search ADS PubMed Akogbéto, M. C., Djouaka R. F., and Kinde-Gazard D. A.. 2006. Screening of pesticide residues in soil and water samples from agricultural setting. Malar. J . 24: 22. Google Scholar CrossRef Search ADS Barbazan, P., Baldet T., Darriet F., Escaffre H., Haman Djoda D., and Hougard J. M.. 1998. Impact of treatment with Bacillus sphaericus on Anopheles gambiae populations and the transmission of malaria in Maroua, a large city in a savannah region of Cameroon. J. Am. Mosq. Control Assoc . 14: 33– 39. Google Scholar PubMed Barrera, R., Amador M., and Clark C. G.. 2006. Ecological factors influencing Aedes aegypti (Diptera: Culicidae) productivity in artificial containers in Salinas, Puerto Rico. J. Med. Entomol . 43: 484– 492. Google Scholar CrossRef Search ADS PubMed Bentley, M. D., and Day J. F.. 1989. Chemical ecology and behavioral aspects of mosquito oviposition. Annu. Rev. Entomol . 34: 401– 421. Google Scholar CrossRef Search ADS PubMed Chadee, D. D., Lakhan A., Ramdath W. R., and Persad R. C.. 1993. Oviposition response of Aedes aegypti mosquitoes to different concentrations of hay infusion in Trinidad, West Indies. J. Am. Mosq. Control Assoc . 9: 346– 348. Google Scholar PubMed Clements, A. N. 2000. The biology of mosquitoes. Development, nutrition and reproduction . CABI Publishing, Eastbourne, UK. Corbel, V., F. Darriet, F. Chandre, and Hougard J. M.. 2002. Insecticide mixtures for mosquito net impregnation against malaria vectors. Parasite . 9: 255– 259. Google Scholar CrossRef Search ADS PubMed Cordellier, R., Germain M., Hervy J. P., and Mouchet J.. 1977. Guide pratique pour l’étude des vecteurs de fièvre jaune en Afrique et méthode de lutte. ORSTOM Editions, Initiation, Documents techniques, Paris, France. Costa, F., Fattore G., and Abril M.. 2012. Diversity of containers and buildings infested with Aedes aegypti in Puerto Iguazú, Argentina. Cad. Saude Publica . 28: 1802– 1086. Google Scholar CrossRef Search ADS PubMed Darriet, F., and Corbel V.. 2008a. [Aedes aegypti oviposition in response to NPK fertilizers]. Parasite . 15: 89– 92. Google Scholar CrossRef Search ADS Darriet, F., and Corbel V.. 2008b. [Attractive properties and physicochemical modifications of water following colonization by Aedes aegypti larvae (Diptera: Culicidae)]. C. R. Biol . 331: 617– 622. Google Scholar CrossRef Search ADS Darriet, F., Zumbo B., Corbel V., and Chandre F.. 2010. Influence of plant matter and NPK fertilizer on the biology of Aedes aegypti (Diptera: Culicidae). Parasite . 17: 149– 154. Google Scholar CrossRef Search ADS PubMed Darriet, F., Rossignol M., and Chandre F.. 2012. The combination of NPK fertilizer and deltamethrin insecticide favors the proliferation of pyrethroid-resistant Anopheles gambiae (Diptera: Culicidae). Parasite . 19: 159– 164. Google Scholar CrossRef Search ADS PubMed Darriet, F. 2014. Des moustiques et des hommes. Chronique d’une pullulation annoncée . IRD Éditions. collection Didactiques, Marseille, France. Google Scholar CrossRef Search ADS Darriet, F. 2016. An anti-mosquito mixture for domestic use, combining a fertiliser and a chemical or biological larvicide. Pest Manag. Sci . 72: 1340– 1345. Google Scholar CrossRef Search ADS PubMed Delatte, H., J. S. Dehecq, J. Thiria, C. Domerg, C. Paupy, and Fontenille D.. 2008. Geographic distribution and developmental sites of Aedes albopictus (Diptera: Culicidae) during a Chikungunya epidemic event. Vector Borne Zoonotic Dis . 8: 25– 34. Google Scholar CrossRef Search ADS PubMed Diabate, A., Baldet T., Chandre F., Akogbeto M., Guigemde T. R., Darriet F., Brengues C., Hemingway J., Small G. J., and Hougard J. M.. 2002. The role of agriculture use of insecticide to pyrethroids in Anopheles gambiae s.l. in Burkina Faso. Am. J. Trop. Med. Hyg . 67: 617– 622. Google Scholar CrossRef Search ADS PubMed Dossou-Yovo, J., J. M. Doannio, S. Diarrassouba, and Chauvancy G.. 1998. [The impact of rice fields on malaria transmission in the city of Bouaké, Côte d’Ivoire]. Bull. Soc. Pathol. Exot . 91: 327– 333. Google Scholar PubMed FAO. 2012. Current world fertilizer trends and outlook to 2016 . Food and Agriculture Organization of the United Nations, Rome. Grube, A., Donaldson D., Kiely T., and Wu L.. 2011. Pesticide industry sales and usage: 2006 and 2007 market estimates . Environmental Protection Agency, Washington, DC. Hao, X. H., Hu R. G., Wu J. S., Tang S. R., and Luo X. Q.. 2010. Effects of long-term fertilization on paddy soils organic nitrogen, microbial biomass, and microbial functional diversity. J. Appl. Ecol . 21: 1477– 1484. Hayes, E. B. 2009. Zika virus outside Africa. Emerg. Infect. Dis . 15: 1347– 1350. Google Scholar CrossRef Search ADS PubMed Kibuthu, T. W., Nejenga S. M., Mbugua A. K., and Muturi E. J.. 2016. Agricultural chemicals: life changer for mosquito vectors in agricultural landscapes? Parasit. vectors . 9: 500. Google Scholar CrossRef Search ADS Maciel-de-Freitas, R., and Lourenço-de-Oliveira R.. 2011. Does targeting key-containers effectively reduce Aedes aegypti population density? Trop. Med. Int. Health . 16: 965– 973. Google Scholar CrossRef Search ADS Mwangagi, J. M., Muturi E. J., Shililu J., Muriu S. M., Jacob B., Kabiru E. W., Mbogo C. M., Githure J., and Novak K.. 2006. Survival of immature Anopheles arabiensis (Diptera: Culicidae) in aquatic habitats in Mwea rice irrigation scheme, central Kenya. Malar. J . 5: 114. Google Scholar CrossRef Search ADS PubMed Raymond, M., Prato G., and Ratsira D.. 1997. Probit and Logit Analysis Program, version 2.0 . Praxème, Biometric, Centre National de la Recherche Scientifique, Montpellier, France. Reiter, P. 2010. Yellow fever and dengue: a threat to Europe? Euro Surveill . 15: 19509. Google Scholar PubMed Sanford, M. R., Chan K., and Walton W. E.. 2005. Effects of inorganic nitrogen enrichment on mosquitoes (Diptera: Culicidae) and the associated aquatic community in constructed treatment wetlands. J. Med. Entomol . 42: 766– 776. Google Scholar CrossRef Search ADS PubMed Statistica. 2011. Windows statistical software, version 10 . StatSoft France, Maisons-Alfort. www.statsoft.fr. Accessed 2 December 2017. Victor, T. J., and Reuben R.. 2000. Effects of organic and inorganic fertilisers on mosquito populations in rice fields of southern India. Med. Vet. Entomol . 14: 361– 368. Google Scholar CrossRef Search ADS PubMed Vollset, S. E. 1993. Confidence intervals for a binomial proportion. Stat. Med . 12: 809– 824. Google Scholar CrossRef Search ADS PubMed WHO. 2011. World malaria report 2011 . World Health Organization, Geneva. Young, G. B., Golladay S., Covich A., and Blackmore M.. 2014. Nutrient enrichment affects immature mosquito abundance and species composition in field-based mesocosms in the coastal plain of Georgia. Environ. Entomol . 43: 1– 8. Google Scholar CrossRef Search ADS PubMed © The Author(s) 2017. Published by Oxford University Press on behalf of Entomological Society of America. All rights reserved. For permissions, please e-mail: firstname.lastname@example.org.
Journal of Medical Entomology – Oxford University Press
Published: Mar 1, 2018
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